[go: up one dir, main page]

JP2608459B2 - Waste liquid treatment method - Google Patents

Waste liquid treatment method

Info

Publication number
JP2608459B2
JP2608459B2 JP12180788A JP12180788A JP2608459B2 JP 2608459 B2 JP2608459 B2 JP 2608459B2 JP 12180788 A JP12180788 A JP 12180788A JP 12180788 A JP12180788 A JP 12180788A JP 2608459 B2 JP2608459 B2 JP 2608459B2
Authority
JP
Japan
Prior art keywords
copper
waste liquid
culture
cells
present
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP12180788A
Other languages
Japanese (ja)
Other versions
JPH01293195A (en
Inventor
豊秋 久保田
Original Assignee
豊秋 久保田
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by 豊秋 久保田 filed Critical 豊秋 久保田
Priority to JP12180788A priority Critical patent/JP2608459B2/en
Publication of JPH01293195A publication Critical patent/JPH01293195A/en
Application granted granted Critical
Publication of JP2608459B2 publication Critical patent/JP2608459B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Landscapes

  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は、廃液の処理方法に関するものであるが、更
に詳細には、特定の微生物を用いて非常に有害な廃液を
効率よく処理する方法に関するものである。
Description: TECHNICAL FIELD The present invention relates to a method for treating waste liquid, and more particularly, to a method for efficiently treating a very harmful waste liquid using a specific microorganism. It is about.

(従来の技術) 従来、汚水処理方法としては、機械的方法、凝集沈澱
といった化学的方法、活性汚泥や微生物を用いる生物学
的方法が知られている(「化学大辞典2」共立出版(昭
42−9−10)p149)。
(Prior Art) Conventionally, as a sewage treatment method, a mechanical method, a chemical method such as coagulation sedimentation, and a biological method using activated sludge or microorganisms are known ("Chemical Dictionary 2", Kyoritsu Shuppan (Showa
42-9-10) p149).

しかしながら、シアンや銅等を含有する廃液は、活性
汚泥や各種微生物に対する毒性がきわめて強いために、
現在多用されている生物学的方法では処理することがで
きない。また他の方法では効率が悪く、工業的な大量処
理には不適である。
However, waste liquids containing cyanide, copper, etc. are extremely toxic to activated sludge and various microorganisms.
It cannot be processed by the biological methods currently used frequently. Other methods are inefficient and unsuitable for industrial mass processing.

(発明が解決しようとする問題点) 上記のように、毒性の強い廃液を有効に処理する工業
的方法は開発されていないのが現状である。
(Problems to be Solved by the Invention) As described above, at present, no industrial method for effectively treating highly toxic waste liquid has been developed.

毒性の強い廃液の中でも特にシアンや銅を含む廃液
は、化学メッキ工場から発生する頻度が高いものであ
る。しかるにメッキ工場は市街地に立地していることが
多く且つ小規模な工場も多いために、大規模な廃水処理
施設を作ることができず、したがって廃水の浄化が充分
に行われず、付近の河川へのシアン(CN-)や銅イオン
のたれ流し事故が跡を絶たない。
Among the highly toxic waste liquids, the waste liquids containing cyan and copper are particularly frequently generated from chemical plating plants. However, plating plants are often located in urban areas and there are many small factories, making it impossible to build large-scale wastewater treatment facilities. of cyanide (CN -) runaway accident or copper ions do not cut off the mark.

それでも、大規模な処理施設があれば、機械的、物理
的な方法であってもこれをくり返すことによって廃水の
浄化が一応可能であろうが、小規模な施設ではそれもで
きないのが技術の現状である。
Nevertheless, if there is a large-scale treatment facility, it may be possible to purify wastewater by repeating the process even if it is mechanical or physical, but technology cannot be achieved with a small facility. Is the current situation.

(問題点を解決するための手段) 本発明は、これらの技術の現状に鑑み、上記した問題
点を一挙に解決するためになされたものである。
(Means for Solving the Problems) The present invention has been made in view of the current state of the art, and has been made in order to solve the above problems at once.

そこで各方面から検討した結果、特に小規模な施設で
の処理に適したシステムとしては、強力な生物学的方法
を利用するシステムが有利であるとの認識を得た。
Therefore, as a result of examination from various fields, it was recognized that a system using a powerful biological method is particularly advantageous as a system suitable for processing in a small-scale facility.

しかしながら、活性汚泥法では、シアンや銅が汚泥の
毒となってしまい、所期の目的を達成することはできな
い。微生物の利用法も同様であるが、無限に存在する微
生物の中にはシアンや銅を無毒化できる菌が存在するの
ではないかとの観点にたった。
However, in the activated sludge method, cyanide and copper become poisons for sludge, and the intended purpose cannot be achieved. The method of using microorganisms is the same, but he pointed out that there may be bacteria that can detoxify cyanogen and copper among microorganisms that exist indefinitely.

そこで、本発明者は、莫大な数の微生物の中から下水
処理菌や脱臭菌として有用な菌を広くスクリーニングし
たところ、下水処理菌として使用して、スカムを大巾に
低減することができ、しかも脱臭効果にすぐれているの
みでなく、まさに決定的なことに、シアンや銅の害作用
を受けないどころか積極的にこれらを無毒化しうる一菌
株を土壌から分離することに成功した。
Therefore, the present inventor has screened a wide range of microorganisms useful as sewage treatment bacteria and deodorizing bacteria from a vast number of microorganisms, and can use them as sewage treatment bacteria to greatly reduce scum. Moreover, not only is it excellent in deodorizing effect, but also decisively, it has succeeded in isolating from the soil a strain that can not only harm cyanide and copper but also positively detoxify them.

ここに分離した一菌株は、菌学的性質においてはバチ
ラス・ズブチリスに属すものと認められたが、スカムの
低減、脱臭等のすぐれた有用性を有するのみでなく、シ
アンや銅を無毒化するという全く新規な有用性も有して
おり、これらの卓越した新規な性質についてはバチラス
・ズブチリスの従来の菌株には認められないので、この
分離株を、バチラス・ズブチリスの新菌株と認め、これ
をバチラス・ズブチリス・クボタと命名した。
One strain isolated here was identified as belonging to Bacillus subtilis in mycological properties, but not only has excellent usefulness such as scum reduction and deodorization, but also detoxifies cyanide and copper. It also has a completely new utility of, and these outstanding novel properties are not found in conventional strains of Bacillus subtilis, so this isolate was recognized as a new strain of Bacillus subtilis, Was named Bacillus subtilis kubota.

本菌株は、Bacillus subtilis Kubota FERM P−9643
として微工研に寄託されている。
This strain is Bacillus subtilis Kubota FERM P-9463.
Has been deposited with the National Institute of Advanced Industrial Science.

次にバチラス・ズブチリス・クボタの菌学的性質を示
す。
Next, the bacteriological properties of Bacillus subtilis kubota are described.

(a)形態 1. 細胞の形及び大きさ 短小桿菌、1.2〜1.4×3.6〜3.8μm 2. 細胞の多形性 特別にない。細胞膜にとりかこまれ、核を持つ。ま
た、芽胞を持ち、特徴的なものであり、Septumを観察で
きる。
(A) Morphology 1. Cell shape and size Short bacillus, 1.2-1.4 × 3.6-3.8 μm 2. Cell polymorphism There is no particular. Involved in the cell membrane and has a nucleus. In addition, it has spores and is characteristic, and Septum can be observed.

3. 運動性の有無 運動性あり、鞭毛は10本位である。3. Existence of motility There is motility, about 10 flagella.

4. 胞子の有無 胞子あり。4. Spore presence Spores are present.

5. グラム染色性 グラム陽性。フェイバーGセット(日水)により青に
染色。
5. Gram staining Gram positive. Stained blue with Faber G Set (Nissui).

6. 抗酸性 チール、ネルゼン染色により赤に染まる。抗酸性の菌
である。
6. Acid-resistant stains red with teal and Nelsen stains. It is an acid-fast bacterium.

(b)各培地における生育状態 生理食塩水に浮遊させた状態で肉汁寒天平板に接種
し、37℃で24時間培養し、よく生育する。
(B) Growth state in each medium Inoculate a broth agar plate in a state of being suspended in physiological saline, culture at 37 ° C. for 24 hours, and grow well.

集落周辺部が円形とならないR型を示す。色は不透
明、淡黄色である。
This shows an R-type in which the periphery of the settlement does not become circular. The color is opaque, pale yellow.

羊血液寒天培養、ハートインヒュージョン寒天培養、
トリプトソーヤ寒天培養でR型、不透明、淡黄色を示
し、いずれも発育良好である。各培地における生育状態
は次の通りである。
Sheep blood agar culture, heart-in fusion agar culture,
It shows R-type, opaque, and pale yellow color on tryptosome agar culture, and all have good growth. The growth state in each medium is as follows.

本発明において使用する新分離株バチラス・ズブチリ
ス・クボタは一般栄養培地であればいかなる培地でも良
好に生育する。特に鶏糞抽出液、畜糞抽出液などはすぐ
れた抽出液となる。
The new isolate Bacillus subtilis kubota used in the present invention grows well on any nutrient medium. In particular, chicken manure extract, animal manure extract, etc. are excellent extracts.

培養は20〜40℃、好ましくは30〜38℃程度で、10〜24
時間開放下に放置しておいても良好に増殖する。
The culture is performed at 20 to 40 ° C, preferably at about 30 to 38 ° C, for 10 to 24
Proliferates well even when left open for hours.

得られた培養物は、大量の菌体を含有しているので、
そのまま下水処理場、浄化槽等に添加してCNやCuを有効
に除去することができる。
The resulting culture contains a large amount of cells,
It can be added to sewage treatment plants and septic tanks as it is to effectively remove CN and Cu.

また、培養物は遠心分離によって菌体を分離して、よ
く洗滌し、澱粉、タルク等の増量剤と混合し、微生物製
剤とすることができる。
In addition, the culture can be separated from cells by centrifugation, washed well, and mixed with a bulking agent such as starch or talc to obtain a microbial preparation.

本発明のバチラス・ズブチリス・クボタはあらゆる剤
形においてよく生存し、使用にあたっては水、空気、土
壌の浄化にすぐれた作用を発揮する。
The Bacillus subtilis kubota of the present invention survives well in all dosage forms and, when used, has an excellent effect on water, air and soil purification.

本発明に係る菌体及び/又はその培養物は、そのまま
で廃水の処理に使用してもよいし、場合によっては活性
炭、ガラスビーズ等常用される担体の表面に付着、凝集
させる等、廃水処理の常法にしたがって廃水処理に有利
に使用できる。本菌による廃水処理の詳細なメカニズム
は、今後の研究にまたねばならないが、シアンにあって
は菌の作用によって炭素と窒素に分解し、また銅につい
ては菌がこれを菌体内に取り込むものと一応推定され、
菌体を沈降除去すれば銅が無害化されるのである。
The cells and / or cultures thereof according to the present invention may be used as they are for the treatment of wastewater, or may be used for wastewater treatment, such as by adhering and coagulating on the surface of commonly used carriers such as activated carbon and glass beads. Can be advantageously used for wastewater treatment according to the conventional method. The detailed mechanism of wastewater treatment by this bacterium must be studied in the future.However, in the case of cyanide, the fungus decomposes into carbon and nitrogen by the action of the bacterium, and in the case of copper, the bacterium takes it into the cells. Once estimated,
If the cells are sedimented and removed, the copper is rendered harmless.

このようにしてシアンや銅イオンを除去した後は、そ
のまま放流してもよいし、必要ある場合には活性汚泥処
理、沈降処理、凝集処理等廃水処理の常法にしたがって
更に処理することはもちろん可能である。
After removing the cyan and copper ions in this manner, it may be discharged as it is, or if necessary, may be further treated according to a conventional method of wastewater treatment such as activated sludge treatment, sedimentation treatment, coagulation treatment. It is possible.

本発明のバチラス・ズブチリス・クボタの菌体のみに
よるマウス経口投与試験において、LD50は、ほぼ無限大
であり、また、マウス皮膚塗布試験においても全く変化
はなかった。
In a mouse oral administration test using only the cells of Bacillus subtilis kubota of the present invention, the LD 50 was almost infinite, and there was no change in the mouse skin application test.

次に本発明の培養例及び実施例を示す。 Next, culture examples and examples of the present invention will be described.

培養例 澱粉 10g 肉エキス 3g ペプトン 10g 塩化ナトリウム 5g 水 1000ml (pH7.0) 以上の組成の培地を500mlフラスコに入れ、これにバ
チラス・ズブチリス・クボタFERM P−9643接種し、37℃
で20時間静置培養した。
Culture example Starch 10 g Meat extract 3 g Peptone 10 g Sodium chloride 5 g Water 1000 ml (pH 7.0) A medium having a composition of not less than 500 ml is placed in a 500 ml flask, and Bacillus subtilis kubota FERM P-9463 is inoculated into the flask, and 37 ° C.
For 20 hours.

得られた培養液を遠心分離して菌体を分離し、菌体を
澱粉300gと混合し、微生物製剤とした。
The obtained culture was centrifuged to separate the cells, and the cells were mixed with 300 g of starch to prepare a microbial preparation.

実施例 NaCNを水に溶解したシアン溶液(CN-として50ppm)、
及びCuCNを水に溶解した銅溶液(銅として10ppm)をそ
れぞれ100mlずつ採取した。
Cyan solution Example NaCN was dissolved in water (CN - 50 ppm as)
And 100 ml of a copper solution (10 ppm as copper) in which CuCN was dissolved in water, respectively.

一方、前記培養例において菌体を分離しておき、これ
を上記廃液にそれぞれ5g/の割合で添加した後、恒温
層に入れて放置し、1日、3日及び5日後にシアン及び
銅の残留量をそれぞれ測定した。通気は、1日1回ビー
カー内にエアーを吹き込んで行った。
On the other hand, in the above-mentioned culture example, the cells were separated, added to the waste solution at a rate of 5 g / each, then placed in a thermostat, and allowed to stand for 1 day, 3 days, and 5 days later. The amount of each residue was measured. Ventilation was performed by blowing air into the beaker once a day.

また、常にエアーを吹き込んで通気培養を行う以外は
上記と同様に5日間処理を行った。
In addition, the treatment was performed for 5 days in the same manner as described above, except that aeration culture was performed by constantly blowing air.

そして、それぞれの処理について次表の結果を得た。 Then, the results shown in the following table were obtained for each processing.

上記した結果からも明らかなように、シアン、銅のい
ずれについても、本発明によって処理すれば、5日後に
はほぼ完全に除去することができることが判る。特にシ
アンについては、わずか1日の処理で90%以上が無害化
されるという著効が得られる。
As is clear from the above results, it is understood that both of cyan and copper can be almost completely removed after 5 days by treating according to the present invention. In particular, with respect to cyan, a remarkable effect that 90% or more is rendered harmless by only one day of treatment is obtained.

また、通気処理を継続すれば更に効果が高まり、シア
ンについては50ppm→0.23ppmに激減し、Cuにいたっては
10ppm→0ppmと完璧に除去無害化されることが明瞭に判
り、本発明の効果の卓越した顕著性が実証された。
Further, if the ventilation process is continued, the effect will be further enhanced, and for cyan, the concentration will be drastically reduced from 50 ppm to 0.23 ppm, and for copper,
It was clearly seen that the removal and detoxification were completely completed from 10 ppm to 0 ppm, demonstrating the outstanding remarkability of the effect of the present invention.

(発明の効果) 上記したように本発明によれば、従来未知の新菌株を
使用することによって、生物毒性の強い銅、シアン廃水
によって菌体の死滅が予測されるのに対してそれどころ
か全くそれとは逆に、これらを無毒化するのに成功した
ものである。
(Effect of the Invention) As described above, according to the present invention, the use of a conventionally unknown new strain allows the cells to be killed by copper and cyanide wastewater, which are highly biotoxic, but rather completely kills the cells. Are, on the contrary, successful in detoxifying them.

しかもその効率がきわめて高いので処理能率がきわめ
て高く、短時間に大量の廃液を処理することができ、小
規模な処理施設で充分所期の目的が達成できる。
Moreover, since the efficiency is extremely high, the processing efficiency is extremely high, a large amount of waste liquid can be processed in a short time, and the intended purpose can be sufficiently achieved in a small-scale processing facility.

したがって、本発明は、大工場や地方公共団体等での
大規模な処理に利用できることはもちろんのこと、小規
模なメッキ工場においても非常に有利に利用することが
できる。
Therefore, the present invention can be used not only in large-scale processing in a large factory or a local public organization, but also very advantageously in a small-scale plating factory.

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】シアン及び/又は銅含有廃液をバチラス・
ズブチリス・クボタ(Bacillus subtilis Kubota)で処
理することを特徴とするシアン及び/又は銅含有廃液の
処理方法。
(1) A waste liquid containing cyan and / or copper is treated with Bacillus
A method for treating a waste liquid containing cyan and / or copper, which is treated with Bacillus subtilis Kubota.
JP12180788A 1988-05-20 1988-05-20 Waste liquid treatment method Expired - Lifetime JP2608459B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP12180788A JP2608459B2 (en) 1988-05-20 1988-05-20 Waste liquid treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP12180788A JP2608459B2 (en) 1988-05-20 1988-05-20 Waste liquid treatment method

Publications (2)

Publication Number Publication Date
JPH01293195A JPH01293195A (en) 1989-11-27
JP2608459B2 true JP2608459B2 (en) 1997-05-07

Family

ID=14820416

Family Applications (1)

Application Number Title Priority Date Filing Date
JP12180788A Expired - Lifetime JP2608459B2 (en) 1988-05-20 1988-05-20 Waste liquid treatment method

Country Status (1)

Country Link
JP (1) JP2608459B2 (en)

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5217623A (en) * 1991-05-30 1993-06-08 Northwestern Flavors, Inc. Method of detoxifying cyanide waste
JP2879321B2 (en) * 1996-03-14 1999-04-05 久保田 豊秋 Oral composition for animals
JP4572135B2 (en) * 2005-03-31 2010-10-27 大成建設株式会社 Method for detoxifying cyanide compounds
JP4799378B2 (en) * 2006-11-22 2011-10-26 旭化成クリーン化学株式会社 Sewage treatment method
CN106630187A (en) * 2016-12-12 2017-05-10 东莞市红树林环保科技有限公司 A lake and landscape water ecological restoration method
CN108220197A (en) * 2018-01-10 2018-06-29 南京林业大学 A kind of gold tailings slag microorganism combined processing and application process
CN108342342B (en) * 2018-03-16 2020-05-22 青岛农业大学 Copper-rich bacillus subtilis and culture method thereof

Also Published As

Publication number Publication date
JPH01293195A (en) 1989-11-27

Similar Documents

Publication Publication Date Title
Kim et al. The roles of microbes in the removal and inactivation of viruses in a biological wastewater treatment system
De-Bashan et al. Microalgae growth-promoting bacteria as “helpers” for microalgae: a novel approach for removing ammonium and phosphorus from municipal wastewater
Narasimhulu et al. Isolation and Identification of Bacterial Strains and Study of their Resistance to Heavy Metals and Antibiotics. J Microbial Biochem Technol 2: 074-076. doi: 10.4172/1948-5948.1000027
Mosso et al. Heterotrophic bacterial populations in the mineral waters of thermal springs in Spain
JP2608459B2 (en) Waste liquid treatment method
CN109706096A (en) One plant of brevibacterium frigoritolerans and its application with denitrogenation and efficient flocculating ability
CN111471611A (en) Rhodococcus ruber HDRR1 for purifying inorganic nitrogen and phosphorus in tail water of seawater pond culture and application thereof
JP2002301494A (en) Activated sludge and wastewater treatment method
CN110938567B (en) A kind of Bacillus subtilis, microbial inoculum and application thereof
JPH10295367A (en) New microorganism belonging to genus bacillus
JPH0622769A (en) Method for biodegradation of phenolic compound, new strain used therefor and method for obtaining microorganism having ability to degrade phenolic compound
JP2000270849A (en) New microorganism
JPH01144971A (en) Useful microorganism
KR100693865B1 (en) New strain Pseudomonas fluorescens HB0210-SK09 [WFCC-11368P] with excellent killing ability of freshwater harmful diatoms, diatoms control method using the same and biological material for controlling diatoms using the same
CN108410758B (en) Triazole-degrading bacteria and their application in the treatment of triazole-containing wastewater
KR20010097621A (en) Bacterium removing chemical softener and chemical dextrin, and manufacture method of its immobilized cells
WO1997014658A1 (en) Cyanide containing effluent purification process
KR102652220B1 (en) Novel Shinella granuli CK-4 strain with high capability of 1,4-dioxane decomposition and method for treating 1,4-dioxane-containing wastewater using the same
CN118388053B (en) A sewage treatment method beneficial to reducing sludge production
JP3944428B2 (en) Microorganisms capable of resolving female hormone substances and use thereof
JP3414618B2 (en) Method for treating ethylene glycol-containing water and microorganism
CN113174350B (en) Alicyclobacillus for degrading anionic surfactant and application thereof
JPH09135682A (en) Method for purely separating and culturing 2-methylisoborneol-degrading microorganism and water purification apparatus using the degrading microorganism
JP2000270848A (en) New microorganism
CN114703090B (en) A moderately halophilic nitrobenzene-degrading bacterium and its application

Legal Events

Date Code Title Description
R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

FPAY Renewal fee payment (prs date is renewal date of database)

Year of fee payment: 12

Free format text: PAYMENT UNTIL: 20090213

EXPY Cancellation because of completion of term
FPAY Renewal fee payment (prs date is renewal date of database)

Year of fee payment: 12

Free format text: PAYMENT UNTIL: 20090213